Benefits of Seed Dispersal for Escaping Seed Predation And

Benefits of Seed Dispersal for Escaping Seed Predation And

Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. Benefits of seed dispersal for escaping seed predation and examining the life history, host suitability/preference and impact of the polyphagous obligate seed predator Cryptaspasma querula A thesis presented in partial fulfilment of the requirements for the degree of Master of Science in Ecology at Massey University, Manawatu, New Zealand Robert B. Silberbauer 2013 ii “Thecreationofathousandforestsisinoneacorn” Ͳ RalphWaldoEmerson iii iv Abstract Cryptaspasma querula is an endemic moth (Family Tortricidae) that is the only known polyphagous obligate post-dispersal seed predator in New Zealand. It is suggested to have multiple hosts including tawa (Beilschmiedia tawa), taraire (Beilschmiedia tarairi), miro (Prumnopitys ferruginea), hinau (Elaeocarpus dentatus), karaka (Corynocarpus laevigatus), and acorns from exotic oaks (Quercus sp.). There have been few studies clarifying these claims and fewer still showing the effects C. querula has on the host plants’ seeds’ germination and establishment. Little is also known about the life history, host preferences, specialist predators/parasitoids and host cues of C. querula. The drilling damage C. querula does to its hosts has been noted in several studies but none have recorded the extent of this damage over the course of the season or what the end percentage of damaged seeds are. Of the described hosts, the broadleaf tree tawa has had been studied the most. The apparent rarity of good germination and establishment under the parent canopy has been noted previously. It is unclear however, whether the impact of seed predators make dispersing seed away from the parent canopy (where fewer seed predators are in theory) more beneficial for tawa. If it is more beneficial, then the extent of dispersal through faunal influences will be important to know. Life history and host cues (in the form of wind tunnel tests used to test olfactory attractants) of C. querula were examined in a controlled environment where rearing observations were taken and variables could easily be manipulated. The host preference and suitability for C. querula was examined in two settings: Laboratory and Field. The controlled environment utilised the seeds of tawa, taraire, hinau, and miro to see whether these were plausible hosts. The field experiments utilised the species miro, karaka, and acorns from exotic oaks. The examination of potential specialist predators or parasitoids took place in two settings: Field and Glass house (semi-controlled environment). In captivity, mating of C. querula adults raised from field collected larvae frequently occurred and many eggs were produced which could be used in choice v tests and behavioural assays. Females lay a variable number of eggs and seemed to prefer ovipositing on smooth surfaces. The time spent in each instar and pupation varied greatly among individuals. Wind tunnel tests were inconclusive for both adult and larvae specimens. However, in choice tests and even when given no other hosts, many of the proposed hosts of C. querula appeared to be unsuitable and were not occupied by C querula larvae in the lab. These included miro, hinau, and karaka where C. querula either ignored the fruits provided, or, if endosperm was utilised, the larvae did not complete their lifecycle. The only suitable and preferred hosts in these trials were tawa and taraire. However, it is highly likely acorns from exotic oaks are also suitable and preferred by C. querula since field trials showed frequent occupancy in acorns. Only one potential competitor (no specialist predators/parasitoids) of C. querula was discovered and it was a generalist facultative diptera (Sylvicola sp.). In a factorial field experiment (repeated at three sites) in which fruit density, the presence or absence of fruit flesh, and the position either under or away from a tawa canopy were assessed, germination and establishment of tawa were highest in high seed density treatments showing potential predator satiation may be occurring. Seeds dispersed away from tawa canopy also had a higher establishment rate than seeds under the parent canopy, suggesting the importance of faunal dispersers The effect of flesh removal was variable but generally favoured establishment. Several additional factors such as vertebrate seed predators/predators, abiotic influences, and site differences appeared to have influenced the results. Drilled/damaged seeds could still germinate/establish but their chances were much lower than undamaged seeds. In these same three sites, plus an additional 8 sites added to widen the study, seed predation at the end of season was very high despite a very heavy fruiting season. As the season progressed, over 90% of tawa seeds ended up being drilled by C. querula suggesting the likelihood of very heavy influences on tawa regeneration. The proportion of bird dispersed seeds was also unexpectedly low (maximum of 8% of seeds beneath the canopy were bird dispersed). The surrounding floral species composition (and dominance) did not appear to influence the damage received to tawa seeds. vi Information on C. querula’s life history, host preferences/suitability and the impact on hosts are better understood through this thesis. Seed dispersal and high seed density are shown to offer the best strategy for tawa seeds’ establishment and survival. The extent of drilling damage on tawa fruits over the course of the season has been shown to be higher than expected and strongly detrimental and demonstrates the importance of predation escape. Thus, tawa is highly dependent on the remaining kereru populations and will be sensitive to further declines to dispersal service. vii viii Acknowledgements This Master of Science thesis could not have been come to pass without the assistance of Alastair Robertson and Steve Trewick who have been exceptional supervisors in their guidance and assistance throughout the research and study process. I would like to thank them for the time, patience and expertise they employed in helping me in this thesis. I would like to thank the following post-graduate students for their time in assisting me with advice, their time, and/or comments: Daniel Smiley, Kyleisha Jaydid, Briar Smith and Matthew Krna. Their influence in this thesis has been of great help. I’d like to thank the four Massey technicians: Tracy Harris, Shaun Nielsen, Cleland Wallace and Paul Barrett for their technician expertise and assistance. Without their help many of the experiments in this thesis would not have been able to be performed. My two field helpers Natalie Eustace and Daniel Smiley have been an amazing help and I’d like to thank them for accompanying me through horrible terrain and less than desirable weather. They made the process much more efficient and enjoyable and I’d highly recommend them for future work. Furthermore I’d like to make a special mention of my friend Natalie Eustace who has been a great support and motivator for me during my research and write up. She not only helped me with field work but provided me with pleasant company during long trips and camping trips; she gave sound advice during my write up and provided continual support and joy during hardships. The full extent of my appreciation goes to her. My family and close friends have all been of great support and help throughout the thesis process and I’d like to thank them all individually: Shirley Silberbauer, Stan Silberbauer, Malcolm Silberbauer, Clare Silberbauer, Mary Dwen, Erin Loveridge, Melinda Rawlings, Amanda Martens, Hayley Stewart, Rosanne Eustace, Glen Eustace, Bethani Eustace, Alastair Manning, Carolin Doerfel, Inge Anderson, Grant ix Douglas, Mike Dodd, Ross Gray, Chris Carran, Josef Beautrais, and everyone in Auckland and Palmerston North who helped me in this thesis. I’d also like to thank Rhys Mills for his assistance at Nga Manu Reserve. Many thanks to the Palmerston North City council for the permits to access Turitea Water Catchment; and the Department of Conservation for the permits to access many of the sites used in this thesis. This thesis is dedicated to my sister Clare Silberbauer, who is loveliest, most wonderful person I have ever known. x TableofContents Abstract.........................................................................................................iv Acknowledgements........................................................................................ix 1.Introduction......................................................................................................1 1.1InvertebrateSeedPredators.....................................................................1 1.2IntroductiontoCryptaspasmaquerula.....................................................4 1.3FocalHostͲSpecies.....................................................................................8 2. Testing host species of Cryptaspasma querula & analysing its life historyinalaboratoryandfieldsetting........................................................11 2.1Introduction............................................................................................11 2.2Methods..................................................................................................14 2.2.1InͲLabRearingandExperiments.....................................................14

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